Method for purifying contaminated polyethylene

ABSTRACT

A method for purifying reclaimed polyethylene, such as polyethylene reclaimed from post-consumer use or post-industrial use, is disclosed. The method involves obtaining the reclaimed polyethylene and contacting it at an elevated temperature and pressure with a fluid solvent to produce an extracted reclaimed polyethylene. The extracted reclaimed polyethylene is dissolved in a solvent at an elevated temperature and pressure to produce a polyethylene solution, which is purified at an elevated temperature and pressure by contacting the polyethylene solution with solid media to produce a purer polyethylene solution. A purer polyethylene is then separated from the purer polyethylene solution.

FIELD OF THE INVENTION

The present invention generally relates to a method for purifying contaminated polymers through the use of a pressurized solvent and solid media. More specifically, this invention relates to a method for purifying recycled polymers, such as post-consumer and post-industrial recycled plastics, to produce a colorless or clear, odor free, virgin-like polymer. It is particularly useful for the purification of polyethylene.

BACKGROUND OF THE INVENTION

Polymers, especially synthetic plastics, are ubiquitous in daily life due to their relatively low production costs and good balance of material properties. Synthetic plastics are used in a wide variety of applications, such as packaging, automotive components, medical devices, and consumer goods. To meet the high demand of these applications, tens of billions of pounds of synthetic plastics are produced globally on an annual basis. The overwhelming majority of synthetic plastics are produced from increasingly scarce fossil sources, such as petroleum and natural gas. Additionally, the manufacturing of synthetic plastics from fossil sources produces CO₂ as a by-product.

The ubiquitous use of synthetic plastics has consequently resulted in millions of tons of plastic waste being generated every year. While the majority of plastic waste is landfilled via municipal solid waste programs, a significant portion of plastic waste is found in the environment as litter, which is unsightly and potentially harmful to ecosystems. Plastic waste is often washed into river systems and ultimately out to sea.

Plastics recycling has emerged as one solution to mitigate the issues associated with the wide-spread usage of plastics. Recovering and re-using plastics diverts waste from landfills and reduces the demand for virgin plastics made from fossil-based resources, which consequently reduces greenhouse gas emissions. In developed regions, such as the United States and the European Union, rates of plastics recycling are increasing due to greater awareness by consumers, businesses, and industrial manufacturing operations. The majority of recycled materials, including plastics, are mixed into a single stream which is collected and processed by a material recovery facility (MRF). At the MRF, materials are sorted, washed, and packaged for resale. Plastics can be sorted into individual materials, such as high-density polyethylene (HDPE) or poly(ethylene terephthalate) (PET), or mixed streams of other common plastics, such as polypropylene (PP), low-density polyethylene (LDPE), poly(vinyl chloride) (PVC), polystyrene (PS), polycarbonate (PC), and polyamides (PA). The single or mixed streams can then be further sorted, washed, and reprocessed into a pellet that is suitable for re-use in plastics processing, for example blow and injection molding.

Though recycled plastics are sorted into predominately uniform streams and are washed with aqueous and/or caustic solutions, the final reprocessed pellet often remains highly contaminated with unwanted waste impurities, such as spoiled food residue and residual perfume components. In addition, recycled plastic pellets, except for those from recycled beverage containers, are darkly colored due to the mixture of dyes and pigments commonly used to colorize plastic articles. While there are some applications that are insensitive to color and contamination (for example black plastic paint containers and concealed automotive components), the majority of applications require non-colored pellets. The need for high quality, “virgin-like” recycled resin is especially important for food and drug contact applications, such as food packaging. In addition to being contaminated with impurities and mixed colorants, many recycled resin products are often heterogeneous in chemical composition and may contain a significant amount of polymeric contamination, such as recycled polypropylene contamination in polyethylene and vice versa.

Mechanical recycling, also known as secondary recycling, is the process of converting recycled plastic waste into a re-usable form for subsequent manufacturing. A more detailed review of mechanical recycling and other plastics recovery processes are described in S. M. Al-Salem, P. Lettieri, J. Baeyens, “Recycling and recovery routes of plastic solid waste (PSW): A review”, Waste Management, Volume 29, Issue 10, October 2009, Pages 2625-2643, ISSN 0956-053X. While advances in mechanical recycling technology have improved the quality of recycled polymers to some degree, there are fundamental limitations of mechanical decontamination approaches, such as the physical entrapment of pigments within a polymer matrix. Thus, even with the improvements in mechanical recycling technology, the dark color and high levels of chemical contamination in currently available recycled plastic waste prevents broader usage of recycled resins by the plastics industry.

To overcome the fundamental limitations of mechanical recycling, there have been many methods developed to purify contaminated polymers via chemical approaches, or chemical recycling. Most of these methods use solvents to decontaminate and purify polymers. The use of solvents enables the extraction of impurities and the dissolution of polymers, which further enables alternative separation technologies.

For example, U.S. Pat. No. 7,935,736 describes a method for recycling polyester from polyester-containing waste using a solvent to dissolve the polyester prior to cleaning. The '736 patent also describes the need to use a precipitant to recover the polyester from the solvent.

In another example, U.S. Pat. No. 6,555,588 describes a method to produce a polypropylene blend from a plastic mixture comprised of other polymers. The '588 patent describes the extraction of contaminants from a polymer at a temperature below the dissolution temperature of the polymer in the selected solvent, such as hexane, for a specified residence period. The '588 patent further describes increasing the temperature of the solvent (or a second solvent) to dissolve the polymer prior to filtration. The '588 patent yet further describes the use of shearing or flow to precipitate polypropylene from solution. The polypropylene blend described in the '588 patent contained polyethylene contamination up to 5.6 wt %.

In another example, European Patent Application No. 849,312 (translated from German to English) describes a process to obtain purified polyolefins from a polyolefin-containing plastic mixture or a polyolefin-containing waste. The '312 patent application describes the extraction of polyolefin mixtures or wastes with a hydrocarbon fraction of gasoline or diesel fuel with a boiling point above 90° C. at temperatures between 90° C. and the boiling point of the hydrocarbon solvent. The '312 patent application further describes contacting a hot polyolefin solution with bleaching clay and/or activated carbon to remove foreign components from the solution. The '312 patent yet further describes cooling the solution to temperatures below 70° C. to crystallize the polyolefin and then removing adhering solvent by heating the polyolefin above the melting point of the polyolefin, or evaporating the adhering solvent in a vacuum or passing a gas stream through the polyolefin precipitate, and/or extraction of the solvent with an alcohol or ketone that boils below the melting point of the polyolefin.

In another example, U.S. Pat. No. 5,198,471 describes a method for separating polymers from a physically commingled solid mixture (for example waste plastics) containing a plurality of polymers using a solvent at a first lower temperature to form a first single phase solution and a remaining solid component. The '471 patent further describes heating the solvent to higher temperatures to dissolve additional polymers that were not solubilized at the first lower temperature. The '471 patent describes filtration of insoluble polymer components.

In another example, U.S. Pat. No. 5,233,021 describes a method of extracting pure polymeric components from a multi-component structure (for example waste carpeting) by dissolving each component at an appropriate temperature and pressure in a supercritical fluid and then varying the temperature and/or pressure to extract particular components in sequence. However, similar to the '471 patent, the '021 patent only describes filtration of undissolved components.

In another example, U.S. Pat. No. 5,739,270 describes a method and apparatus for continuously separating a polymer component of a plastic from contaminants and other components of the plastic using a co-solvent and a working fluid. The co-solvent at least partially dissolves the polymer and the second fluid (that is in a liquid, critical, or supercritical state) solubilizes components from the polymer and precipitates some of the dissolved polymer from the co-solvent. The '270 patent further describes the step of filtering the thermoplastic-co-solvent (with or without the working fluid) to remove particulate contaminants, such as glass particles.

The known solvent-based methods to purify contaminated polymers, as described above, do not produce “virgin-like” polymer. In the previous methods, co-dissolution and thus cross contamination of other polymers often occurs. If adsorbent is used, a filtration and/or centrifugation step is often employed to remove the used adsorbent from solution. In addition, isolation processes to remove solvent, such as heating, vacuum evaporation, and/or precipitation using a precipitating chemical are used to produce a polymer free of residual solvent.

Accordingly, a need still exists for an improved solvent-based method to purify contaminated polymers that uses a solvent that is readily and economically removed from the polymer, is relatively simple in terms of the number of unit operations, produces a polymer without a significant amount of polymeric cross contamination, produces a polymer that is essentially colorless, and produces a polymer that is essentially odorless.

SUMMARY OF THE INVENTION

A method for purifying reclaimed polyethylene is disclosed. The method comprises obtaining the reclaimed polyethylene wherein the reclaimed polyethylene is selected from the group consisting of post-consumer use polymers, post-industrial use polymers, and combinations thereof. The reclaimed polyethylene is contacted at a temperature from about 80° C. to about 220° C. and at a pressure from about 150 psig (1.03 MPa) to about 15,000 psig (103.42 MPa) with a first fluid solvent having a standard boiling point less than about 70° C., to produce an extracted reclaimed polyethylene. The extracted reclaimed polyethylene is dissolved in a solvent selected from the group consisting of the first fluid solvent, a second fluid solvent, and mixtures thereof, at a temperature from about 90° C. to about 220° C. and a pressure from about 350 psig (2.41 MPa) to about 20,000 psig (137.90 MPa) to produce a polyethylene solution. The polyethylene solution is purified at a temperature from about 90° C. to about 220° C. and at a pressure from about 350 psig (2.41 MPa) to about 20,000 psig (137.90 MPa) by contacting the polyethylene solution with solid media to produce a purer polyethylene solution. Then a purer polyethylene is separated from the purer polyethylene solution. In one embodiment, the second fluid solvent has either the same chemical composition or a different chemical composition as the first fluid solvent.

In one embodiment, the purer polyethylene is separated from the purer polyethylene solution at a temperature from about 0° C. to about 220° C. and a pressure from about 0 psig (0 MPa) to 2,000 psig (13.79 MPa).

In one embodiment, the reclaimed polyethylene is post-consumer recycle derived polyethylene. In another embodiment, the reclaimed polyethylene is a polyethylene homopolymer or a primarily polyethylene copolymer.

In one embodiment, the fluid solvent has a standard boiling point less than about 0° C. and greater than about −45° C. and a standard enthalpy change of vaporization of less than about +25 kJ/mol. In another embodiment, the fluid solvent is selected from the group consisting of olefinic hydrocarbons, aliphatic hydrocarbons, and mixtures thereof.

In one embodiment, the aliphatic hydrocarbon is selected from the group consisting of C₁-C₆ aliphatic hydrocarbons and mixtures thereof. In another embodiment, the aliphatic hydrocarbons and mixtures thereof is comprised of primarily C₄ aliphatic hydrocarbons.

In one embodiment, the fluid solvent consists essentially of C₄ liquefied petroleum gas. In another embodiment, the fluid solvent is n-butane, butane isomers, or mixtures thereof.

In one embodiment, the temperature in the extraction, dissolution, and purification steps is from about 110° C. to about 170° C. In one embodiment, the pressure in the contacting step is from about 1,100 psig (7.58 MPa) to about 5,500 psig (37.92 MPa). In another embodiment, the pressure in the contacting step is less than about 1,100 psig (7.58 MPa).

In one embodiment, the pressure in the dissolving step is greater than about 4,500 psig (31.03 MPa). In another embodiment, the pressure in the dissolving step is greater than about 5,500 psig (37.92 MPa).

In one embodiment, the solid media is selected from the group consisting of inorganic substances, carbon-based substances, and mixtures thereof. In another embodiment, the inorganic substances are selected from the group consisting of oxides of silicon, oxides of aluminum, oxides of iron, aluminum silicates, amorphous volcanic glasses, and mixtures thereof. In another embodiment, the inorganic substances are selected from the group consisting of silica, silica gel, diatomite, sand, quartz, alumina, perlite, fuller's earth, bentonite, and mixtures thereof. In another embodiment, the inorganic substance is reclaimed glass.

In one embodiment, the carbon-based substances are selected from the group consisting of anthracite coal, carbon black, coke, activated carbon, cellulose, and mixtures thereof. In another embodiment, the contacting of the polyethylene solution with the solid media is done in a packed bed of the solid media. In one embodiment, the packed bed is greater than 20 cm in length.

Additional features of the invention may become apparent to those skilled in the art from a review of the following detailed description, taken in conjunction with the examples.

BRIEF DESCRIPTION OF THE DRAWINGS

FIG. 1 is a block flow diagram showing the major steps of one embodiment of the present invention.

FIG. 2 is a schematic of the experimental apparatus used in the examples.

FIG. 3 is a photograph of the example specimens.

FIG. 4 is a bar chart of the opacity and odor intensity of the examples.

DETAILED DESCRIPTION OF THE INVENTION I. Definitions

As used herein, the term “reclaimed polymer” refers to a polymer used for a previous purpose and then recovered for further processing.

As used herein, the term “reclaimed polyethylene” refers to a polyethylene polymer used for a previous purpose and then recovered for further processing.

As used herein, the term “post-consumer” refers to a source of material that originates after the end consumer has used the material in a consumer good or product.

As used herein, the term “post-consumer recycle” (PCR) refers to a material that is produced after the end consumer has used the material and has disposed of the material in a waste stream.

As used herein, the term “post-industrial” refers to a source of a material that originates during the manufacture of a good or product.

As used herein, the term “fluid solvent” refers to a substance that may exist in the liquid state under specified conditions of temperature and pressure. In some embodiments the fluid solvent may be a predominantly homogenous chemical composition of one molecule or isomer, while in other embodiments, the fluid solvent may be a mixture of several different molecular compositions or isomers. Further, in some embodiments of the present invention, the term “fluid solvent” may also apply to substances that are at, near, or above the critical temperature and critical pressure (critical point) of that substance. It is well known to those having ordinary skill in the art that substances above the critical point of that substance are known as “supercritical fluids” which do not have the typical physical properties (i.e. density) of a liquid.

As used herein, the term “dissolved” means at least partial incorporation of a solute (polymeric or non-polymeric) in a solvent at the molecular level. Further, the thermodynamic stability of the solute/solvent solution can be described by the following equation 1: ΔG _(mix) =ΔH _(m) −TΔS _(mix)  (I)

where ΔG_(mix) is the Gibbs free energy change of mixing of a solute with a solvent, ΔH_(mix) is the enthalpy change of mixing, T is the absolute temperature, and ΔS_(mix) is the entropy of mixing. To maintain a stable solution of a solute in a solvent, the Gibbs free energy must be negative and at a minimum. Thus, any combination of solute and solvent that minimize a negative Gibbs free energy at appropriate temperatures and pressures can be used for the present invention.

As used herein, the term “standard boiling point” refers to the boiling temperature at an absolute pressure of exactly 100 kPa (1 bar, 14.5 psia, 0.9869 atm) as established by the International Union of Pure and Applied Chemistry (IUPAC).

As used herein, the term “standard enthalpy change of vaporization” refers to the enthalpy change required to transform a specified quantity of a substance from a liquid into a vapor at the standard boiling point of the substance.

As used herein, the term “polyethylene solution” refers to a solution of polyethylene dissolved in a solvent. The polyethylene solution may contain undissolved matter and thus the polyethylene solution may also be a “slurry” of undissolved matter suspended in a solution of polyethylene dissolved in a solvent.

As used herein, the term “solid media” refers to a substance that exists in the solid state under the conditions of use. The solid media may be crystalline, semi-crystalline, or amorphous. The solid media may be granular and may be supplied in different shapes (i.e. spheres, cylinders, pellets, etc.). If the solid media is granular, the particle size and particle size distribution of solid media may be defined by the mesh size used to classify the granular media. An example of standard mesh size designations can be found in the American Society for Testing and Material (ASTM) standard ASTM E11 “Standard Specification for Woven Wire Test Sieve Cloth and Test Sieves.” The solid media may also be a non-woven fibrous mat or a woven textile.

As used herein, the term “purer polyethylene solution” refers to a polyethylene solution having fewer contaminants relative to the same polyethylene solution prior to a purification step.

As used herein, the term “virgin-like” means essentially contaminant-free, pigment-free, odor-free, homogenous, and similar in properties to virgin polymers.

As used herein, the term “primarily polyethylene copolymer” refers a copolymer with greater than 70 mol % of ethylene repeating units.

II. Method for Purifying Contaminated Polyethylene

Surprisingly, it has been found that certain fluid solvents, which in a preferred embodiment exhibit temperature and pressure-dependent solubility for polymers, when used in a relatively simple process can be used to purify contaminated polyethylene, especially reclaimed or recycled polyethylene, to a near virgin-like quality. This process, exemplified in FIG. 1, comprises 1) obtaining a reclaimed polyethylene (step a in FIG. 1), followed by 2) extracting the polyethylene with a fluid solvent at an extraction temperature (T_(E)) and at an extraction pressure (P_(E)) (step b in FIG. 1), followed by 3) dissolution of the polyethylene in a fluid solvent at a dissolution temperature (T_(D)) and at a dissolution pressure (P_(D)) (step c in FIG. 1), followed by 4) contacting the dissolved polyethylene solution with solid media at a dissolution temperature (T_(D)) and at a dissolution pressure (P_(D)) (step d in FIG. 1), followed by separation of the polyethylene from the fluid solvent (step e in FIG. 1). In one embodiment of the present invention, the purified polyethylene, which may be sourced from post-consumer waste streams, is essentially contaminant-free, pigment-free, odor-free, homogenous, and similar in properties to virgin polymers. Furthermore, in a preferred embodiment, the physical properties of the fluid solvent of the present invention may enable more energy efficient methods for separation of the fluid solvent from the purified polyethylene.

Reclaimed Polyethylene

In one embodiment of the present invention, a method for purifying reclaimed polyethylene includes obtaining reclaimed polyethylene. For the purposes of the present invention, the reclaimed polyethylene is sourced from post-consumer, post-industrial, post-commercial, and/or other special waste streams. For example, post-consumer waste polyethylene can be derived from curbside recycle streams where end-consumers place used polymers from packages and products into a designated bin for collection by a waste hauler or recycler. Post-consumer waste polymers can also be derived from in-store “take-back” programs where the consumer brings waste polymers into a store and places the waste polymers in a designated collection bin. An example of post-industrial waste polymers can be waste polymers produced during the manufacture or shipment of a good or product that are collected as unusable material by the manufacturer (i.e. trim scraps, out of specification material, start up scrap). An example of waste polymers from a special waste stream can be waste polymers derived from the recycling of electronic waste, also known as e-waste. Another example of waste polymers from a special waste stream can be waste polymers derived from the recycling of automobiles. Another example of waste polymers from a special waste stream can be waste polymers derived from the recycling of used carpeting and textiles.

For the purposes of the present invention, the reclaimed polyethylene is a homogenous composition of an individual polymer or a mixture of several different polyethylene compositions. Non-limiting examples of polyethylene compositions are homopolymers and copolymers of ethylene, such as high density polyethylene (HDPE), low density polyethylene (LDPE), linear low density polyethylene (LLDPE), copolymers of ethylene and alpha-olefins, and other dissolvable polyethylene polymers that may be apparent to those having ordinary skill in the art.

The reclaimed polyethylene may also contain various pigments, dyes, process aides, stabilizing additives, fillers, and other performance additives that were added to the polymer during polymerization or conversion of the original polymer to the final form of an article. Non-limiting examples of pigments are organic pigments, such as copper phthalocyanine, inorganic pigments, such as titanium dioxide, and other pigments that may be apparent to those having ordinary skill in the art. A non-limiting example of an organic dye is Basic Yellow 51. Non-limiting examples of process aides are antistatic agents, such as glycerol monostearate and slip-promoting agents, such as erucamide. A non-limiting example of a stabilizing additive is octadecyl-3-(3,5-di-tert.butyl-4-hydroxyphenyl)-propionate. Non-limiting examples of fillers are calcium carbonate, talc, and glass fibers.

Solvent

The fluid solvent of the present invention has a standard boiling point less than about 70° C. Pressurization maintains solvents, which have standard boiling points below the operating temperature range of the present invention, in a state in which there is little or no solvent vapor. In one embodiment, the fluid solvent with a standard boiling point less than about 70° C. is selected from the group consisting of carbon dioxide, ketones, alcohols, ethers, esters, alkenes, alkanes, and mixtures thereof. Non-limiting examples of fluid solvents with standard boing points less than about 70° C. are carbon dioxide, acetone, methanol, dimethyl ether, diethyl ether, ethyl methyl ether, tetrahydrofuran, methyl acetate, ethylene, propylene, 1-butene, 2-butene, isobutylene, 1-pentene, 2-pentene, branched isomers of pentene, 1-hexene, 2-hexene, methane, ethane, propane, n-butane, isobutane, n-pentane, isopentane, neopentane, n-hexane, isomers of isohexane, and other substances that may be apparent to those having ordinary skill in the art.

The selection of the fluid solvent used will dictate the temperature and pressure ranges used to perform the steps of the present invention. A review of polymer phase behavior in solvents of the kind described by the present invention is provided in the following reference: McHugh et al. (1999) Chem. Rev. 99:565-602.

Extraction

In one embodiment of the present invention, a method for purifying polyethylene includes contacting reclaimed polyethylene with a fluid solvent at a temperature and at a pressure wherein the polymer is essentially insoluble in the fluid solvent. Although not wishing to be bound by any theory, applicants believe that the temperature and pressure-dependent solubility can be controlled in such a way to prevent the fluid solvent from fully solubilizing the polymer, however, the fluid solvent can diffuse into the polymer and extract any extractable contamination. The extractable contamination may be residual processing aides added to the polymer, residual product formulations which contacted the polymer, such as perfumes and flavors, dyes, and any other extractable material that may have been intentionally added or unintentionally became incorporated into the polymer, for example, during waste collection and subsequent accumulation with other waste materials.

In one embodiment, the controlled extraction may be accomplished by fixing the temperature of the polymer/fluid solvent system and then controlling the pressure below a pressure, or pressure range, where the polymer dissolves in the fluid solvent. In another embodiment, the controlled extraction is accomplished by fixing the pressure of the polymer/solvent system and then controlling the temperature below a temperature, or temperature range where the polymer dissolves in the fluid solvent. The temperature and pressure-controlled extraction of the polymer with a fluid solvent uses a suitable pressure vessel and may be configured in a way that allows for continuous extraction of the polymer with the fluid solvent. In one embodiment of the present invention, the pressure vessel may be a continuous liquid-liquid extraction column where molten polymer is pumped into one end of the extraction column and the fluid solvent is pumped into the same or the opposite end of the extraction column. In another embodiment, the fluid containing extracted contamination is removed from the process. In another embodiment, the fluid containing extracted contamination is purified, recovered, and recycled for use in the extraction step or a different step in the process. In one embodiment of the present invention, the extraction may be performed as a batch method, wherein the reclaimed polyethylene is fixed in a pressure vessel and the fluid solvent is continuously pumped through the fixed polymer phase. The extraction time or the amount of fluid solvent used will depend on the desired purity of the final purer polymer and the amount of extractable contamination in the starting reclaimed polyethylene. In another embodiment, the fluid containing extracted contamination is contacted with solid media in a separate step as described in the “Purification” section below. In another embodiment, a method for purifying reclaimed polyethylene includes contacting reclaimed polyethylene with a fluid solvent at a temperature and at a pressure wherein the polymer is molten and in the liquid state. In another embodiment, the reclaimed polyethylene is contacted with the fluid solvent at a temperature and at a pressure wherein the polymer is in the solid state.

In one embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with a fluid solvent at a temperature and a pressure wherein the polyethylene remains essentially undissolved. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a temperature from about 80° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a pressure from about 150 psig (1.03 MPa) to about 6,500 psig (44.82 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a pressure from about 3,000 psig (20.68 MPa) to about 6,000 psig (41.37 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with n-butane at a pressure from about 4,500 psig (31.03 MPa) to about 5,500 psig (37.92 MPa).

In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a temperature from about 80° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a pressure from about 1,000 psig (6.89 MPa) to about 15,000 psig (103.42 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a pressure from about 2,000 psig (13.79 MPa) to about 10,000 psig (68.95 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting polyethylene with propane at a pressure from about 5,000 psig (34.47 MPa) to about 9,000 psig (62.05 MPa).

Dissolution

In one embodiment of the present invention, a method for purifying reclaimed polyethylene includes dissolving the reclaimed polyethylene in a fluid solvent at a temperature and at a pressure wherein the polymer is dissolved in the fluid solvent. Although not wishing to be bound by any theory, applicants believe that the temperature and pressure can be controlled in such a way to enable thermodynamically favorable dissolution of the reclaimed polymer in a fluid solvent. Furthermore, the temperature and pressure can be controlled in such a way to enable dissolution of a particular polymer or polymer mixture while not dissolving other polymers or polymer mixtures. This controllable dissolution enables the separation of polymers from polymer mixtures.

In one embodiment of the present invention, a method for purifying polymers includes dissolving contaminated reclaimed polyethylene in a solvent that does not dissolve the contaminants under the same conditions of temperature and pressure. The contaminants may include pigments, fillers, dirt, and other polymers. These contaminants are released from the reclaimed polyethylene upon dissolution and then removed from the polymer solution via a subsequent solid-liquid separation step.

In one embodiment of the present invention, a method for purifying reclaimed polyethylene includes dissolving polyethylene in a fluid solvent at a temperature and at a pressure wherein the polyethylene is dissolved in the fluid solvent. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a temperature from about 90° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a pressure from about 1,000 psig (6.89 MPa) to about 12,000 psig (82.74 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a pressure from about 2,000 psig (13.79 MPa) to about 10,000 psig (68.95 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in n-butane at a pressure from about 4,000 psig (27.58 MPa) to about 6,000 psig (41.37 MPa).

In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a temperature from about 90° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a pressure from about 3,000 psig (20.68 MPa) to about 20,000 psig (137.90 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a pressure from about 5,000 psig (34.47 MPa) to about 15,000 psig (103.42 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes dissolving polyethylene in propane at a pressure from about 8,000 psig (55.16 MPa) to about 11,000 psig (75.84 MPa).

Purification

In one embodiment of the present invention, a method for purifying polyethylene includes contacting a contaminated polymer solution with solid media at a temperature and at a pressure wherein the polymer remains dissolved in the fluid solvent. The solid media of the present invention is any solid material that removes at least some of the contamination from a solution of reclaimed polyethylene dissolved in the fluid solvent of the present invention. Although not wishing to be bound by any theory, the applicants believe that the solid media removes contamination by a variety of mechanisms. Non-limiting examples of possible mechanisms include adsorption, absorption, size exclusion, ion exclusion, ion exchange, and other mechanisms that may be apparent to those having ordinary skill in the art. Furthermore, the pigments and other contaminants commonly found in reclaimed polyethylene may be polar compounds and may preferentially interact with the solid media, which may also be at least slightly polar. The polar-polar interactions are especially favorable when non-polar solvents, such as alkanes, are used as the fluid solvent.

In one embodiment of the present invention, the solid media is selected from the group consisting of inorganic substances, carbon-based substances, or mixtures thereof. Useful examples of inorganic substances include oxides of silicon, oxides of aluminum, oxides of iron, aluminum silicates, magnesium silicates, amorphous volcanic glasses, silica, silica gel, diatomite, sand, quartz, reclaimed glass, alumina, perlite, fuller's earth, bentonite, and mixtures thereof. Useful examples of carbon-based substances include anthracite coal, carbon black, coke, activated carbon, cellulose, and mixtures thereof. In another embodiment of the present invention, the solid media is recycled glass.

In one embodiment of the present invention, the solid media is contacted with the polymer in a vessel for a specified amount of time while the solid media is agitated. In another embodiment, the solid media is removed from the purer polymer solution via a solid-liquid separation step. Non-limiting examples of solid-liquid separation steps include filtration, decantation, centrifugation, and settling. In another embodiment of the present invention, the contaminated polymer solution is passed through a stationary bed of solid media. In another embodiment of the present invention, the height or length of the stationary bed of solid media is greater than 5 cm. In another embodiment of the present invention, the height or length of the stationary bed of solid media is greater than 10 cm. In another embodiment of the present invention, the height or length of the stationary bed of solid media is greater than 20 cm. In another embodiment of the present invention, the solid media is replaced as needed to maintain a desired purity of polymer. In yet another embodiment, the solid media is regenerated and re-used in the purification step. In another embodiment, the solid media is regenerated by fluidizing the solid media during a backwashing step.

In one embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/fluid solvent solution with solid media at a temperature and a pressure wherein the polyethylene remains dissolved in the fluid solvent. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a temperature from about 90° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a pressure from about 1,000 psig (6.89 MPa) to about 12,000 psig (82.74 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a pressure from about 2,000 psig (13.79 MPa) to about 10,000 psig (68.95 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/n-butane solution with solid media at a pressure from about 4,000 psig (27.58 MPa) to about 6,000 psig (41.37 MPa).

In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a temperature from about 90° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a temperature from about 100° C. to about 200° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a temperature from about 130° C. to about 180° C. In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a pressure from about 3,000 psig (20.68 MPa) to about 20,000 psig (137.90 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a pressure from about 5,000 psig (34.47 MPa) to about 15,000 psig (103.42 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes contacting a polyethylene/propane solution with solid media at a pressure from about 8,000 psig (55.16 MPa) to about 11,000 psig (75.84 MPa).

Separation

In one embodiment of the present invention, a method for purifying reclaimed polyethylene includes separating the purer polymer from the fluid solvent at a temperature and at a pressure wherein the polymer precipitates from solution and is no longer dissolved in the fluid solvent. In another embodiment, the precipitation of the purer polymer from the fluid solvent is accomplished by reducing the pressure at a fixed temperature. In another embodiment, the precipitation of the purer polymer from the fluid solvent is accomplished by reducing the temperature at a fixed pressure. In another embodiment, the precipitation of the purer polymer from the fluid solvent is accomplished by increasing the temperature at a fixed pressure. In another embodiment, the precipitation of the purer polymer from the fluid solvent is accomplished by reducing both the temperature and pressure. The solvent can be partially or completely converted from the liquid to the vapor phase by controlling the temperature and pressure. In another embodiment, the precipitated polymer is separated from the fluid solvent without completely converting the fluid solvent into a 100% vapor phase by controlling the temperature and pressure of the solvent during the separation step. The separation of the precipitated purer polymer is accomplished by any method of liquid-liquid or liquid-solid separation. Non-limiting examples of liquid-liquid or liquid-solid separations include filtration, decantation, centrifugation, and settling.

In one embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/fluid solvent solution at a temperature and a pressure wherein the polyethylene precipitates from solution. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a temperature from about 0° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a temperature from about 50° C. to about 175° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a temperature from about 100° C. to about 160° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a pressure from about 0 psig (0 MPa) to about 4,000 psig (27.58 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a pressure from about 50 psig (0.34 MPa) to about 2,000 psig (13.79 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/n-butane solution at a pressure from about 75 psig (0.52 MPa) to about 1,000 psig (6.89 MPa).

In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a temperature from about −42° C. to about 220° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a temperature from about 0° C. to about 150° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a temperature from about 50° C. to about 130° C. In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a pressure from about 0 psig (0 MPa) to about 15,000 psig (103.42 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a pressure from about 50 psig (0.34 MPa) to about 5,000 psig (34.48 MPa). In another embodiment, a method for purifying reclaimed polyethylene includes separating polyethylene from a polyethylene/propane solution at a pressure from about 75 psig (0.52 MPa) to about 1,000 psig (6.89 MPa).

III Test Methods

The test methods described herein are used to measure the effectiveness of various methods for purifying polymers. Specifically, the methods described demonstrate the effectiveness of a given purification method at improving color and translucency/clarity (i.e. making the color and opacity of the reclaimed polyethylene closer to that of an uncolored virgin polymer), reducing or eliminating elemental contamination (i.e. removing heavy metals), reducing or eliminating non-combustible contamination (i.e. inorganic fillers), and reducing or eliminating volatile compounds (especially volatile compounds that contribute to the malodor of reclaimed polyethylene).

Color and Opacity Measurement:

The color and opacity/translucency of a polymer are important parameters that determine whether or not a polymer can achieve the desired visual aesthetics of an article manufactured from the polymer. Reclaimed polyethylene, especially post-consumer derived reclaimed polyethylene, is typically dark in color and opaque due to residual pigments, fillers, and other contamination. Thus, color and opacity measurements are important parameters in determining the effectiveness of a method for purifying polymers.

Prior to color measurement, samples of either polymeric powders or pellets were compression molded into 30 mm wide×30 mm long×1 mm thick square test specimens (with rounded corners). Powder samples were first densified at room temperature (ca. 20-23° C.) by cold pressing the powder into a sheet using clean, un-used aluminum foil as a contact-release layer between stainless steel platens. Approximately 0.85 g of either cold-pressed powder or pellets was then pressed into test specimens on a Carver Press Model C (Carver, Inc., Wabash, Ind. 46992-0554 USA) pre-heated to 200° C. using aluminum platens, unused aluminum foil release layers, and a stainless steel shim with a cavity corresponding to the aforementioned dimensions of the square test specimens. Samples were heated for 5 minutes prior to applying pressure. After 5 minutes, the press was then compressed with at least 2 tons (1.81 metric tons) of hydraulic pressure for at least 5 seconds and then released. The molding stack was then removed and placed between two thick flat metal heat sinks for cooling. The aluminum foil contact release layers were then peeled from the sample and discarded. The flash around the sample on at least one side was peeled to the mold edge and then the sample was pushed through the form. Each test specimen was visually evaluated for voids/bubble defects and only samples with no defects in the color measurement area (0.7″ (17.78 mm) diameter minimum) were used for color measurement.

The color of each sample was characterized using the International Commission on Illumination (CIE) L*, a*, b* three dimensional color space. The dimension L* is a measure of the lightness of a sample, with L*=0 corresponding to the darkest black sample and L*=100 corresponding to the brightest white sample. The dimension a* is a measure of the red or green color of a sample with positive values of a* corresponding with a red color and negative values of a* corresponding with a green color. The dimension b* is a measure of the blue or yellow color of a sample with positive values of b* corresponding with a blue color and negative values of b* corresponding with a yellow color. The L*a*b* values of each 30 mm wide×30 mm long×1 mm thick square test specimen sample were measured on a HunterLab model LabScan XE spectrophotometer (Hunter Associates Laboratory, Inc., Reston, Va. 20190-5280, USA). The spectrophotometer was configured with D65 as the standard illuminant, an observer angle of 10°, an area diameter view of 1.75″ (44.45 mm), and a port diameter of 0.7″ (17.78 mm).

The opacity of each sample, which is a measure of how much light passes through the sample (i.e. a measure of the sample's translucency), was determined using the aforementioned HunterLab spectrophotometer using the contrast ratio opacity mode. Two measurements were made to determine the opacity of each sample. One to measure the brightness value of the sample backed with a white backing, Y_(WhiteBacking), and one to measure the brightness value of the sample backed with a black backing, Y_(BlackBacking). The opacity was then calculated from the brightness values using the following equation 2:

$\begin{matrix} {{\%\mspace{14mu}{Opacity}} = {\frac{Y_{{Black}\mspace{14mu}{Backing}}}{Y_{{White}\mspace{14mu}{Backing}}}*100}} & ({II}) \end{matrix}$ Elemental Analysis:

Many sources of reclaimed polyethylene have unacceptably high concentrations of heavy metal contamination. The presence of heavy metals, for example lead, mercury, cadmium, and chromium, may prevent the use of reclaimed polyethylene in certain applications, such as food or drug contact applications or medical device applications. Thus, measuring the concentration of heavy metals is important when determining the effectiveness of a method for purifying polymers.

Elemental analysis was performed using Inductively Coupled Plasma Mass Spectrometry (ICP-MS). Test solutions were prepared in n=2 to n=6 depending on sample availability by combining ˜0.25 g sample with 4 mL of concentrated nitric acid and 1 mL of concentrated hydrofluoric acid (HF). The samples were digested using an Ultrawave Microwave Digestion protocol consisting of a 20 min ramp to 125° C., a 10 min ramp to 250° C. and a 20 min hold at 250° C. Digested samples were cooled to room temperature. The digested samples were diluted to 50 mL after adding 0.25 mL of 100 ppm Ge and Rh as the internal standard. In order to assess accuracy of measurement, pre-digestion spikes were prepared by spiking virgin polymer. Virgin polymer spiked samples were weighed out using the same procedure mentioned above and spiked with the appropriate amount of each single element standard of interest, which included the following: Na, Al, Ca, Ti, Cr, Fe, Ni, Cu, Zn, Cd, and Pb. Spikes were prepared at two different levels: a “low level spike” and a “high level spike”. Each spike was prepared in triplicate. In addition to spiking virgin polymer, a blank was also spiked to verify that no errors occurred during pipetting and to track recovery through the process. The blank spiked samples were also prepared in triplicate at the two different levels and were treated in the same way as the spiked virgin polymer and the test samples. A 9 point calibration curve was made by making 0.05, 0.1, 0.5, 1, 5, 10, 50, 100, and 500 ppb solutions containing Na, Al, Ca, Ti, Cr, Fe, Ni, Cu, Zn, Cd, and Pb. All calibration standards were prepared by dilution of neat standard reference solutions and 0.25 mL of 100 ppm Ge and Rh as the internal standard with 4 mL of concentrated nitric and 1 mL of concentrated HF. Prepared standards, test samples, and spiked test samples were analyzed using an Agilent's 8800 ICP-QQQMS, optimized according to manufacturer recommendations. The monitored m/z for each analyte and the collision cell gas that was used for analysis was as follows: Na, 23 m/z, H₂; Al, 27 m/z, H₂; Ca, 40 m/z, H₂; Ti, 48 m/z, H₂; Cr, 52 m/z, He; Fe, 56 m/z, H₂; Ni, 60 m/z; no gas; Cu, 65 m/z, no gas; Zn, 64 m/z, He; Cd, 112 m/z; H₂; Pb, sum of 206≧206, 207≧207, 208≧208 m/z, no gas; Ge, 72 m/z, all modes; Rh, 103 m/z, all modes. Ge was used as an internal standard for all elements<103 m/z and Rh was used for all elements>103 m/z.

Residual Ash Content:

Many sources of reclaimed polyethylene contain various fillers, for example calcium carbonate, talcum, and glass fiber. While useful in the original application of the reclaimed polyethylene, these fillers alter the physical properties of a polymer in way that may be undesired for the next application of the reclaimed polyethylene. Thus, measuring the amount of filler is important when determining the effectiveness of a method for purifying polymers.

Thermogravimetric analysis (TGA) was performed to quantify the amount of non-combustible materials in the sample (also sometimes referred to as Ash Content). About 5-15 mg of sample was loaded onto a platinum sample pan and heated to 700° C. at a rate of 20° C./min in an air atmosphere in a TA Instruments model Q500 TGA instrument. The sample was held isothermal for 10 min at 700° C. The percentage residual mass was measured at 700° C. after the isothermal hold.

Odor Analysis:

Odor sensory analysis was performed by placing about 3 g of each sample in a 20 mL glass vial and equilibrating the sample at room temperature for at least 30 min. After equilibration, each vial was opened and the headspace was sniffed (bunny sniff) by a trained grader to determine odor intensity and descriptor profile. Odor intensity was graded according to the following scale:

5=Very Strong

4=Strong

3=Moderate

2=Weak to Moderate

1=Weak

0=No odor

EXAMPLES

The following examples further describe and demonstrate embodiments within the scope of the present invention. The examples are given solely for the purpose of illustration and are not to be construed as limitations of the present invention, as many variations thereof are possible without departing from the spirit and scope of the invention.

Example 1

A sample of post-consumer derived recycled high-density polyethylene was sourced from a supplier of recycled resins. The post-consumer recycled polyethylene was classified as “natural color” and originated from the United Kingdom. The as-received pellets were characterized using the test methods disclosed herein and the resulting data are summarized in Table 1. The purpose of this example is to show the properties of a representative post-consumer derived recycled polyethylene resin before being purification.

The pellets and corresponding square test specimens were off-white in color as indicated in the L*a*b* values of the square test specimens. The opacity of the sample of example 1 was about 81.61% opaque. A photograph of the square test specimen is shown in FIG. 3 as Example 1.

This example serves as a representative baseline for heavy metal contamination found in post-consumer derived recycled polyethylene. When compared to the other example, the heavy metal contamination was found to be greater in the as-received post-consumer derived recycled polyethylene.

The samples of example 1 had ash content values that averaged to about 0.8513 wt %, which also serves as a baseline for the amount of non-combustible substances that may be present in post-consumer derived recycled polyethylene.

This example also serves as a representative baseline for odor compound contamination found in post-consumer derived recycled polyethylene. The samples of example 9 were found to have an odor intensity of 2.5 on a 5 point scale (5 being most intense).

Example 2

The sample of post-consumer derived recycled polyethylene described in example 1 was processed using the experimental apparatus shown in FIG. 2 and the following procedure:

-   -   1. 237 g of the polyethylene pellets were loaded into a 1.1 L         extraction column pressure vessel with an internal diameter (ID)         of 1.75″ (44.45 mm) and a length of 28″ (71.12 cm) that was         heated to an external skin temperature of 175° C.     -   2. Liquid n-butane solvent was pressurized to about 4,500 psig         (31.03 MPa) using a positive displacement pump and pre-heated to         a temperature of about 110° C. using two heat exchangers before         it was introduced to the bottom of the extraction column.     -   3. The fluid stream leaving the top of the extraction column was         introduced into the top of a second 0.5 L pressure vessel with         an ID of 2″ (50.8 mm) and a length of about 8.5″ (21.59 cm) that         was heated to an external skin temperature of 175° C. The second         pressure vessel contained 150 mL of silica gel (Silicycle Ultra         Pure Silica Gels, SiliaFlash GE60, Parc-Technologies, USA) that         was pre-mixed in a beaker with 150 mL of aluminum oxide         (Activated Alumina, Selexsorb CDX, 7×14, BASF, USA).     -   4. The fluid stream leaving the bottom of the second pressure         vessel was depressurized across an expansion valve into a         side-arm Erlenmeyer flask. After depressurizing the fluid stream         into the Erlenmeyer flask, the solvent vapor was vented through         the side-arm port and any liquids/solids were collected in the         flask. The n-butane solvent was eluted through the system at         4,500 psig (31.03 MPa) until no further material was observed         accumulating in the flask. 3.93 g of white solids were collected         and labeled as ‘Fraction 1’.     -   5. The Erlenmeyer flask was replaced with an empty, clean flask         and the system pressure was then increased to 5,000 psig (34.47         MPa).     -   6. The system pressure was maintained at 5,000 psig (34.47 MPa)         until no further solid material was observed eluting from the         system. 33.19 g of white solids were collected and labeled as         ‘Fraction 2’.         The data for the fraction 2 samples collected at 5,000 psig         (34.47 MPa) are summarized in Table 1.

The fraction 2 solids isolated in this example were white to off-white in color. When the fraction 2 solids were compression molded into square test specimens, the specimens were off-white. A photograph of the square test specimen is shown in FIG. 3 as Example 2. As shown in FIG. 3, the specimen was more translucent than the untreated PE and was similar in opacity to virgin polyethylene. The L*a*b* values also show that the square test specimens from fraction 2 of example 2 showed an improvement in color relative to the samples of example 1 (i.e. as-received post-consumer derived polyethylene). The L* values for the square test specimens from fraction 2 of example 2 averaged 85.20 which were improved when compared to the L* values for the sample of example 1, which averaged 80.28. The opacity for the square test specimens from fraction 2 of example 2, which averaged 53.20% opaque, were also improved when compared to the opacity values for the samples of example 1, which averaged about 81.61% opaque.

The concentration of heavy metal contamination in the samples from fraction 2 of example 2 were also improved when compared to the samples of example 1. For example, the concentration of sodium in the samples from fraction 2 of example 2 averaged 6,620 ppb while the concentration of sodium in the samples of example 1 averaged 19,800 ppb (a reduction of about 67%). The concentrations of all of the other elements measured were all reduced by greater than 66% for the samples from fraction 2 of example 2 relative to the samples of example 1.

The samples from fraction 2 of example 2 had ash content values that averaged to about 0.5032 wt %, which were lower than the ash content values for the samples of example 1, which averaged to about 0.8513 wt %.

The samples from fraction 2 of example 2 were found to have an odor intensity of 0.5 on a 5 point scale (5 being most intense), which was improved when compared to the odor intensity of the samples of example 1, which had an odor intensity of 2.5.

FIG. 4 is a bar chart of the opacity and odor intensity of the purified recycled polyethylene of example 2 compared to the untreated recycled polyethylene (example 1), and a virgin polyethylene comparative sample. As shown in FIG. 4, the purified recycled polyethylene of example 2 had an improved opacity and odor intensity.

TABLE 1 Color, contamination, and odor removal of Examples 1 and 2 Example 1 Example 2 Fraction N/A Fraction 2 Solid Media N/A 150 mL of silica gel mixed with 150 mL of aluminum oxide Color L* 80.28 85.20 (n = 1) (n = 1) Color a* −3.85 −2.37 (n = 1) (n = 1) Color b*  5.47  4.62 (n = 1) (n = 1) Opacity (Y) 81.61 53.20 Na (ppb) 19,800 ± 2,380 6,620 ± 1,320 LOQ = 100 ppb (n = 5) (n = 5) Al (ppb) 37,600 ± 3,010 7,100 ± 142  LOQ = 1000 ppb (n = 5) (n = 5) Ca (ppb) 126,000 ± 0    13,600 ± 952   LOQ = 1000 ppb (n = 5) (n = 5) Ti (ppb) 1,040,000 ± 41,600  171,000 ± 5,130  LOQ = 100 ppb (n = 5) (n = 5) Cr (ppb)  3,070 ± 1,600 1,030 ± 144  LOQ = 10 ppb (n = 5) (n = 5) Fe (ppb) 18,400 ± 552  4,040 ± 1,490 LOQ = 1000 ppb (n = 5) (n = 5) Ni (ppb)  28.9 ± 11.9 <LOQ LOQ = 10 ppb (n = 5) Cu (ppb)  391 ± 31.3 86.5 ± 4.33 LOQ = 10 ppb (n = 5) (n = 5) Zn (ppb) 14,800 ± 1,330 2,970 ± 238  LOQ = 10 ppb (n = 5) (n = 5) Cd (ppb) <LOQ <LOQ LOQ = 10 ppb Pb (ppb)  197 ± 29.6 40.3 ± 1.21 LOQ = 10 ppb (n = 5) (n = 5) Ash Content  0.8513 ± 0.0898 0.5032 ± 0.1356 (% res from TGA) (n = 2) (n = 2) Odor Intensity 2.5 0.5 (0-5) Virgin Polyethylene Comparative Samples

Dow 6850A polyethylene (The Dow Chemical Company, USA) was used for all “Virgin PE” comparative samples. The pellets of virgin PE were processed into square test specimens according the methods described herein. The L*a*b* values for the specimens made from virgin PE averaged to 84.51±0.97, −1.03±0.04, and −0.63±0.12, respectively The square test specimens had an average opacity of 34.68±0.69% opaque. The pellets of virgin PE had an odor intensity of 0.5 on a 5 point scale (5 being the most intense) and had odor described as being like “plastic.”

Every document cited herein, including any cross reference or related patent or patent application, is hereby incorporated herein by reference in its entirety unless expressly excluded or otherwise limited. The citation of any document is not an admission that it is prior art with respect to any invention disclosed or claimed herein or that it alone, or in any combination with any other reference or references, teaches, suggest or discloses any such invention. Further, to the extent that any meaning or definition of a term in this document conflicts with any meaning or definition of the same term in a document incorporated by reference, the meaning or definition assigned to that term in this document shall govern.

While particular embodiments of the present invention have been illustrated and described, it would be obvious to those skilled in the art that various other changes and modification can be made without departing from the spirit and scope of the invention. It is therefore intended to cover in the appended claims all such changes and modification that are within the scope of the present invention. 

What is claimed is:
 1. A method for purifying reclaimed polyethylene comprising: a. obtaining the reclaimed polyethylene wherein said reclaimed polyethylene is selected from the group consisting of post-consumer use polymers, post-industrial use polymers, and combinations thereof; b. contacting the reclaimed polyethylene at a temperature from about 80° C. to about 220° C. and at a pressure from about 150 psig (1.03 MPa) to about 15,000 psig (103.42 MPa) with a first fluid solvent having a standard boiling point less than about 70° C., to produce an extracted reclaimed polyethylene; c. dissolving the extracted reclaimed polyethylene in a solvent selected from the group consisting of the first fluid solvent, a second fluid solvent, and mixtures thereof, at a temperature from about 90° C. to about 220° C. and a pressure from about 350 psig (2.41 MPa) to about 20,000 psig (137.90 MPa) to produce a polyethylene solution; d. purifying said polyethylene solution at a temperature from about 90° C. to about 220° C. and at a pressure from about 350 psig (2.41 MPa) to about 20,000 psig (137.90 MPa) by contacting said polyethylene solution with solid media to produce a purer polyethylene solution; and e. separating a purer polyethylene from said purer polyethylene solution; wherein said second fluid solvent has the same chemical composition as or a different chemical composition than the first fluid solvent.
 2. The method of claim 1, wherein the purer polyethylene is separated from said purer polyethylene solution at a temperature from about 0° C. to about 220° C. and a pressure from about 0 psig (0 MPa) to 2,000 psig (13.79 MPa).
 3. The method of claim 1, wherein the reclaimed polyethylene is post-consumer recycle derived polyethylene.
 4. The method of claim 1, wherein said polyethylene is a polyethylene homopolymer or a primarily polyethylene copolymer.
 5. The method of claim 1, wherein said fluid solvent has a standard boiling point less than about 0° C. and greater than about −45° C. and a standard enthalpy change of vaporization of less than about +25 kJ/mol.
 6. The method of claim 1, wherein said fluid solvent is selected from the group consisting of olefinic hydrocarbons, aliphatic hydrocarbons, and mixtures thereof.
 7. The method of claim 6, wherein said aliphatic hydrocarbon is selected from the group consisting of C₁-C₆ aliphatic hydrocarbons and mixtures thereof.
 8. The method of claim 6, wherein said aliphatic hydrocarbons and mixtures thereof is comprised of primarily C₄ aliphatic hydrocarbons.
 9. The method of claim 6, wherein said fluid solvent consists essentially of C₄ liquefied petroleum gas.
 10. The method of claim 8, wherein said fluid solvent is n-butane, butane isomers, or mixtures thereof.
 11. The method of claim 1, wherein said temperature in steps b, c, and d is from about 110° C. to about 170° C.
 12. The method of claim 1, wherein said pressure in step b is from about 1,100 psig (7.58 MPa) to about 5,500 psig (37.92 MPa).
 13. The method of claim 1, wherein said pressure in step b is from about 150 psig (1.03 MPa) to about 1,100 psig (7.58 MPa).
 14. The method of claim 1, wherein said pressure in step c is from about 4,500 psig (31.03 MPa) to about 20,000 psig (137.90 MPa).
 15. The method of claim 1, wherein said pressure in step c is from about 5,500 psig (37.92 MPa) to about 20,000 psig (137.90 MPa).
 16. The method of claim 1, wherein said solid media is selected from the group consisting of inorganic substances, carbon-based substances, and mixtures thereof.
 17. The method of claim 16, wherein said inorganic substances are selected from the group consisting of oxides of silicon, oxides of aluminum, oxides of iron, aluminum silicates, amorphous volcanic glasses, and mixtures thereof.
 18. The method of claim 16, wherein said inorganic substances are selected from the group consisting of silica gel, diatomite, sand, quartz, alumina, perlite, fuller's earth, bentonite, and mixtures thereof.
 19. The method of claim 18, wherein said inorganic substance is reclaimed glass.
 20. The method of claim 16, wherein said carbon-based substances are selected from the group consisting of anthracite coal, carbon black, coke, activated carbon, cellulose, and mixtures thereof.
 21. The method of claim 1, wherein said contacting of the polyethylene solution with said solid media is performed in a packed bed of said solid media.
 22. The method of claim 21, where said packed bed is greater than 20 cm in length. 